AU2020307195A1 - Steam cracking process comprising a separation step and differential treatment of the obtained particles according to a threshold value - Google Patents
Steam cracking process comprising a separation step and differential treatment of the obtained particles according to a threshold value Download PDFInfo
- Publication number
- AU2020307195A1 AU2020307195A1 AU2020307195A AU2020307195A AU2020307195A1 AU 2020307195 A1 AU2020307195 A1 AU 2020307195A1 AU 2020307195 A AU2020307195 A AU 2020307195A AU 2020307195 A AU2020307195 A AU 2020307195A AU 2020307195 A1 AU2020307195 A1 AU 2020307195A1
- Authority
- AU
- Australia
- Prior art keywords
- particles
- steam cracking
- threshold value
- biomass
- process according
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000002245 particle Substances 0.000 title claims abstract description 60
- 238000000034 method Methods 0.000 title claims abstract description 46
- 238000004230 steam cracking Methods 0.000 title claims abstract description 41
- 238000000926 separation method Methods 0.000 title description 8
- 239000002029 lignocellulosic biomass Substances 0.000 claims abstract description 9
- 239000002028 Biomass Substances 0.000 claims description 25
- 238000012216 screening Methods 0.000 claims description 4
- 238000002485 combustion reaction Methods 0.000 claims description 3
- 239000012620 biological material Substances 0.000 claims description 2
- 239000000843 powder Substances 0.000 abstract description 19
- 239000007787 solid Substances 0.000 abstract description 8
- 239000002551 biofuel Substances 0.000 abstract description 5
- 239000000047 product Substances 0.000 description 11
- 238000006243 chemical reaction Methods 0.000 description 10
- 239000008188 pellet Substances 0.000 description 10
- 238000005453 pelletization Methods 0.000 description 7
- 239000000463 material Substances 0.000 description 6
- 238000000197 pyrolysis Methods 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 150000001875 compounds Chemical class 0.000 description 4
- 239000007788 liquid Substances 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 238000004880 explosion Methods 0.000 description 3
- 239000000835 fiber Substances 0.000 description 3
- 238000002791 soaking Methods 0.000 description 3
- 230000009466 transformation Effects 0.000 description 3
- 239000002023 wood Substances 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000036983 biotransformation Effects 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000013529 heat transfer fluid Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 229920002488 Hemicellulose Polymers 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- 238000011138 biotechnological process Methods 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000003575 carbonaceous material Substances 0.000 description 1
- 238000002144 chemical decomposition reaction Methods 0.000 description 1
- 238000010924 continuous production Methods 0.000 description 1
- 238000000280 densification Methods 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000004146 energy storage Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 238000005194 fractionation Methods 0.000 description 1
- 238000007429 general method Methods 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 230000003301 hydrolyzing effect Effects 0.000 description 1
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 238000010335 hydrothermal treatment Methods 0.000 description 1
- 238000011044 inertial separation Methods 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 239000012263 liquid product Substances 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 230000000135 prohibitive effect Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000011949 solid catalyst Substances 0.000 description 1
- 238000003797 solvolysis reaction Methods 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/02—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
- C10L5/442—Wood or forestry waste
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B49/00—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
- C10B49/02—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with hot gases or vapours, e.g. hot gases obtained by partial combustion of the charge
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
- C10L5/06—Methods of shaping, e.g. pelletizing or briquetting
- C10L5/08—Methods of shaping, e.g. pelletizing or briquetting without the aid of extraneous binders
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
- C10L5/34—Other details of the shaped fuels, e.g. briquettes
- C10L5/36—Shape
- C10L5/363—Pellets or granulates
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B07—SEPARATING SOLIDS FROM SOLIDS; SORTING
- B07B—SEPARATING SOLIDS FROM SOLIDS BY SIEVING, SCREENING, SIFTING OR BY USING GAS CURRENTS; SEPARATING BY OTHER DRY METHODS APPLICABLE TO BULK MATERIAL, e.g. LOOSE ARTICLES FIT TO BE HANDLED LIKE BULK MATERIAL
- B07B1/00—Sieving, screening, sifting, or sorting solid materials using networks, gratings, grids, or the like
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B07—SEPARATING SOLIDS FROM SOLIDS; SORTING
- B07B—SEPARATING SOLIDS FROM SOLIDS BY SIEVING, SCREENING, SIFTING OR BY USING GAS CURRENTS; SEPARATING BY OTHER DRY METHODS APPLICABLE TO BULK MATERIAL, e.g. LOOSE ARTICLES FIT TO BE HANDLED LIKE BULK MATERIAL
- B07B2230/00—Specific aspects relating to the whole B07B subclass
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B2101/00—Type of solid waste
- B09B2101/85—Paper; Wood; Fabrics, e.g. cloths
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
- B09B3/45—Steam treatment, e.g. supercritical water gasification or oxidation
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2200/00—Components of fuel compositions
- C10L2200/04—Organic compounds
- C10L2200/0461—Fractions defined by their origin
- C10L2200/0469—Renewables or materials of biological origin
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/30—Pressing, compressing or compacting
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/54—Specific separation steps for separating fractions, components or impurities during preparation or upgrading of a fuel
- C10L2290/546—Sieving for separating fractions, components or impurities during preparation or upgrading of a fuel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Combustion & Propulsion (AREA)
- Materials Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geochemistry & Mineralogy (AREA)
- Geology (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Wood Science & Technology (AREA)
- Forests & Forestry (AREA)
- Ecology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Processing Of Solid Wastes (AREA)
- Polysaccharides And Polysaccharide Derivatives (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
Abstract
The invention relates to the field of solid biofuels obtained by steam cracking. More particularly, the invention relates to a process for the treatment of lignocellulosic biomass by steam cracking in which the obtained powder is treated in order to separate the particles into two categories according to a threshold value, and each category is treated differently.
Description
The present invention relates to the field of solid biofuels obtained by steam cracking. More particularly, the present invention relates to a process for the treatment of lignocellulosic biomass by steam cracking, in which the obtained powder is treated in order to separate the particles into two categories according to a threshold value, each category being treated differently.
Field of the invention
The production of energy (electrical and thermal) of renewable origin can be achieved from the environment (sun, wind, tide, swell, geothermal, hydraulic) or from biomass. With the exception of biomass, river or barrage hydraulics, and geothermal, these renewable energies are intermittent, unless the energy storage means develop. Only biomass is a primary energy which can be transported to the site of its transformation into heat and/or electricity. However, the biomass is in fact an energy which is not very dense, is variable, and is perishable. The transformation of lignocellulosic biomass (wood, agricultural waste, co-products of agriculture and the agro-industry) into an energy-dense, transportable, and easily storable compound, makes it possible to develop and consolidate a stationary energy industrial sector (biofuel used at a fixed point, at home, in contrast with biofuel oils), and to reduce the environmental impacts (C02 fossil emission, with a biomass without fertilizers or phytosanitaries).
The heat treatment of the biomass by steam cracking allows for this densification of energy, by homogenizing the biomass into a steam-cracked powder according to precise parametric conditions, in particular size grading, temperature, and residence time. The powder is then pelletized in order to facilitate the transport, storage and use thereof.
It is thus a question of ensuring that the steam cracking method is capable of ensuring a constant product, i.e. an output powder that is stable in terms of quality, and is capable of being transformed or used downstream of the method, for the desired application. This powder has a calorific value and a composition suitable for being used in combustion, and is able to be pelletized.
Today, the best solution for guaranteeing the best result of the steam cracking is to make a regular and controlled supply of biomass of the same quality. However, with a view to increasing the volumes of treatment of biomass, for the purpose of production of solid biofuels, it appears to be of interest to be able to also treat a heterogeneous biomass.
The parameters of the steam cracking process are critical, and, in order to facilitate the comparison of different options, a model has been developed that is based on the hypotheses that the kinetics of the process is of the first order and obeys the Arrhenius law, making it possible to develop the ordinate of the reaction (RO):
RD=It exp [(Tr - Tb)/14.75] dt
Where Tr is the reaction temperature (°C), Tb is the baseline temperature (boiling point of water at atmospheric pressure: 100 0C), t is the residence time (min), and 14.75 is the conventional activation energy, supposing that the general method is hydrolytic, and the general conversion is of the first order. The log10 value of the ordinate of the reaction gives the severity factor (or severity) which is used to represent the effects of the steam explosion on the biomass:
Severity = log10 (RO)
The problem encountered when treating a heterogeneous biomass is that the powder obtained is itself heterogeneous, causing problems of pelletization. Indeed, depending on the nature of the initial biomass, and the conditions applies, the steam cracking will not have the same effect in terms of destructuration of the material. Thus, when the input material is heterogeneous, the severity conditions must be adjusted so as to not totally destructure the least resistant materials, which would adversely affect the pelletization. When the severity conditions are adjusted depending on the less resistant biomass, the steam cracking generates residual particles originating from the more resistant biomasses, which also disrupt the pelletization process.
Failure to respect the final quality and the pelletization specifications may be fatal, whether due to a treatment that leaves large particles, or a treatment that is too drastic and degrades the product and its behavior upon pelletization.
There is therefore a need to have access to a steam cracking process which is suitable for treatment of a heterogeneous biomass, for the manufacture of black pellets of a controlled quality.
The steam-cracking differs from hydrothermal pre-treatment, also referred to as aqueous fractionation, solvolysis, hydrothermolysis, or hydrothermal treatment, in that the latter consists in using water at a high temperature and high pressure in order to promote the disintegration and the separation of the lignocellulosic matrix. This technique is not suitable for the production of black pellets, since the products obtained are largely liquid.
The pyrolysis is the chemical decomposition of an organic compound, by intense heating in the absence of oxygen. The compounds obtained following pyrolysis differ, in terms of their characteristics, from those obtained by steam cracking. The steam cracking cannot be likened to a pyrolysis technique, in that it uses steam explosion and is carried out in the presence of oxygen.
It is also necessary to distinguish torrefaction processes, which are characterized by a thermochemical treatment of between 100 and 300°C, which makes it possible to modify some of the organic material in order to break the fibers, while eliminating the water.
Prior art
The Chinese patent CN102 949 969A discloses a system for pyrolysis of solid carbon material or material having an increased viscosity, using a duvet mixer and a catalytic heat transfer fluid heater, and a process for using the reactor system. This process further comprises a solid/solid or solid/liquid separator, for allowing the separation of the solid or liquid pyrolyzed products from the used catalytic heat transfer fluid.
The American patent US2012/260563A1 describes a process for thermochemical transformation of biomass by hydropyrolysis (conventional pyrolysis liquid reaction, with hydrogen and in the presence of solid catalysts) in order to obtain liquid products. This process comprises in particular inertial separation devices.
The patent US2014/298716A1 relates to a process for drying and torrefaction of lignocellulosic biomass. The drying and torrefaction facility comprises two circuits. The second circuit comprises a cyclone separator which makes it possible to eliminate all the large volatile particles.
Finally, the patent US2016/25161lAl discloses a process for growing a microbial organism, comprising the cultivation of the microbial organism in the presence of a hydrolyzed composition obtained from a lignocellulosic feedstock that has undergone a step of steam explosion. The treated lignocellulosic biomass furthermore comprises a step of separation of the fibers depending on a threshold value, such as the size of the fibers.
Disadvantages of the prior art
The solutions of the prior art are not entirely satisfactory, since they use techniques or use a non-pulverulent product. Indeed, these are techniques of: - pyrolysis leading to obtaining compounds different from those obtained by steam cracking - torrefaction, which is a technology having an acceptable yield (10% to 20% loss), but the cost remains prohibitive, and the technology is not mature.
Disclosure of the invention
In order to meet this need, the inventors have developed a process for steam cracking, with a given severity factor, characterized in that it comprises a step of treatment of the pulverulent products in order to separate the particles above a threshold value and the particles below said threshold value, and of differentiated treatment of particles of the first category and particles of the second category.
Said process makes it possible, on the one hand, to pelletize a homogeneous powder from which resistant particles have been removed, and, on the other hand, to treat the overflow of poorly deteriorated material by a return to the steam cracking tank or another deferred treatment.
The invention also relates to a steam cracking facility for implementing this process, comprising a particle separator.
Advantages of the invention
The invention thus consists in implementing a screen for separating the poorly degraded resistant particles from the powder which can be pelletized, or the powder having too fine a size grading from the powder which can be pelletized.
The main advantage of this process is that it makes it possible to produce black pellets of quality, from any type of biomass, and in particular from heterogeneous biomass. Indeed, eliminating the poorly degraded particles from the powder to be pelletized improves the quality of the pellets, which are thus more cohesive, more hydrophobic, and higher-energy.
This process thus makes it possible to comply both with the specifications of the overall pelletization process, and of the specification of the final product, in terms of quality and constancy of quality.
This process makes it possible to recover the poorly degraded particles and to re-use them. It may be a question of subjecting them a second time to a steam cracking treatment, or of using them for other purposes.
It is also possible to eliminate, by the screen, the finest powders which pelletize poorly, and to keep only the powders which are capable of clogging, with the aim of producing pellets. It is possible, for example, to envisage using the finest powders in biotransformation processes.
It will be noted that, if the increase in the severity of the treatment could manage to overcome the issue of particles that remain coarse, this would result in degradation of the more labile wood particles, and would also increase the material loss on account of too advanced degradation of molecules in polymer form into volatile compounds (for example the hemicelluloses that are most sensitive to the temperature and to the residence time). There is therefore an advantage in recycling, into the head of the process, the post-steam cracking screen overflow of the powder, rather than increasing the severity, or indeed subjecting them, in isolation or in a manner grouped together, to more suitable severity conditions.
The invention firstly relates to a process for steam cracking of a lignocellulosic biomass, characterized in that it comprises a step of treatment of the pulverulent products in order to separate the particles above a threshold value and the particles below said threshold value, and of differentiated treatment of particles of the first category and particles of the second category.
A process of this kind comprises the following steps: - steam cracking of a lignocellulosic biomass - screening the pulverulent products obtained by steam cracking, in order to separate the particles above a threshold value (referred to as the "first category") and the particles below said threshold value (referred to as the '"second category")
- differentiated treatment of the particles of the first category and of the particles of the second category.
The severity factor applied during the steam cracking step will be determined depending on the biomass to be treated. It is determined from the value of the Log10 of the ordinate of the reaction.
Severity = log10 (RO)
This is a characteristic that is inherent to the steam cracking process, which a person skilled in the art knows how to measure and adapt. Typically, the severity factor will be between 4.0 and 4.02, and more precisely between 4.05 and 4.15.
This process implements screening which aims to separate the steam cracking particles into two categories, with the aim of differentiated treatment. The threshold value can for example be the mass, the dimension, the cross-sectional area, or the density of the particles, but also their aeraulic behavior, or any other criterion which makes it possible to separate the particles that are too fine, too large, too dense, etc. compared with a threshold value.
In a preferred embodiment, one of the two categories of particles is pelletized for the preparation of black pellets.
In a particular embodiment, the particles to be pelletized correspond to the category of particles that are above the threshold value. It is a question of eliminating the largest and/or the most dense and/or the most resistant particles.
In an alternative embodiment, the particles to be pelletized correspond to the category of particles that are above the threshold value. It is a question of eliminating the particles that are too fine and are not able to be pelletized.
Among the other expected qualities such as the water resistance, the mechanical strength, and the high calorific value, in a general manner the black pellets may be qualified by a main constitution (> 80%) of particles of a size smaller than 500 pm, and a few percent of particles larger than a millimeter, or indeed several millimeters.
The resistance of the pellets to water can be evaluated by soaking, i.e. the product must not take up much water during soaking, and the qualities of the product, such as its mechanical strength, must not be altered following soaking. The mechanical strength of the pellets is associated with an impact resistance and a mechanical durability.
The calorific value of the pellets must be increased with respect to that of the initial biomass.
The severity factor of the steam cracking step is fixed according to the nature of the biomass and the type of powder which it is desired to collect.
The particles which are eliminated undergo a treatment different from pelletization, and are collected and recycled for example by reintroduction into the steam cracking tank, immediately after separation or in a deferred manner, or by re-use in other processes.
There are as many different possibilities for treatment of the eliminated particles as there are particular embodiments of the invention.
In a particular embodiment, the particles above the threshold value (resistant, too large and/or too dense, for example) are reintroduced directly into the steam cracking tank, in order to be treated again within the continuous process.
In another particular embodiment, the particles above or below the threshold value are collected in order to be recycled in a deferred manner. They can be subsequently reintroduced into the steam cracking tank under different severity conditions, or be re used in other processes. The particles that are too fine to be pelletized can for example be used as a substrate for biotransformation reactions, such as biotechnological processes and green chemistry, etc. The particles that are too large can be re-used by means of local combustion in a boiler, or can be reintegrated into biomaterials.
This process thus makes it possible to treat a heterogeneous biomass and to re-use all of this biomass.
Said heterogeneous biomass may consist in a mixture of young woods and old woods, a mixture of woods originating from different species, waste wood, etc.
The invention secondly relates to a steam cracking facility comprising at least one steam cracking unit, and a separator for separating particles into two categories depending on a threshold value, and a means for the transport of the particles thus separated.
The steam cracking facility is a conventional facility with regard to the elements up to the powder collector located at the outlet of the steam cracking tank. The particle separator may be of any type, and depends on the criterion selected for the screen. The screening means may thus be a separation by size selection, such as a rotary screen, a perforated or inclined vibrating table, dynamic densimetric separation such as a ballistic screen, or a centrifugal effect.
The means for differential transport of the particles makes it possible to transport the overflow powder to a site of immediate treatment or to a storage site for deferred treatment. A transport means of this kind may be a conveyor, a chute, a screw, a chain conveyor, a pneumatic system, etc.
The facility may furthermore comprise items of equipment associated with the treatment of said overflow downstream.
Claims (8)
1. Process for steam cracking of a lignocellulosic biomass, characterized in that it comprises: - a step of steam cracking of a lignocellulosic biomass
- a step of screening the pulverulent products obtained at the end of the steam cracking step, in order to separate the particles above a threshold value and the particles below aid threshold value, and - a step of differentiated treatment of the particles of the first category and of the particles of the second category.
2. Process according to claim 1, wherein said threshold value is selected from the mass, the dimension, the cross-sectional area, the density of the particles, the aeraulic behavior of said particles.
3. Process according to either claim 1 or claim 2, wherein one of said categories of particle is pelletized, while the other is eliminated.
4. Process according to claim 3, wherein said eliminated category of particles is collected and recycled via immediate or deferred reintroduction, or re-use in other processes.
5. Process according to claim 4, wherein said eliminated particles are above the threshold value and are re-used in local combustion or integrated into biomaterials.
6. Process according to claim 4, wherein said eliminated particles are below the threshold value and are re-used in biotechnology or green chemistry processes.
7. Process according to any of the preceding claims, wherein said biomass is heterogeneous.
8. Steam cracking facility, characterized in that it comprises at least one steam cracking unit, and a separator for separating particles into two categories depending on a threshold value, and a means for the differential transport of the particles thus separated.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FR1906796A FR3097556B1 (en) | 2019-06-24 | 2019-06-24 | Steam cracking process comprising a step of separation and differential treatment of the particles obtained as a function of a threshold value. |
FR1906796 | 2019-06-24 | ||
PCT/FR2020/051045 WO2020260799A1 (en) | 2019-06-24 | 2020-06-17 | Steam cracking process comprising a separation step and differential treatment of the obtained particles according to a threshold value |
Publications (1)
Publication Number | Publication Date |
---|---|
AU2020307195A1 true AU2020307195A1 (en) | 2022-02-03 |
Family
ID=67810940
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
AU2020307195A Pending AU2020307195A1 (en) | 2019-06-24 | 2020-06-17 | Steam cracking process comprising a separation step and differential treatment of the obtained particles according to a threshold value |
Country Status (11)
Country | Link |
---|---|
US (1) | US20220315851A1 (en) |
EP (1) | EP3986990A1 (en) |
JP (1) | JP2022538234A (en) |
KR (1) | KR20220024849A (en) |
CN (1) | CN114555761A (en) |
AU (1) | AU2020307195A1 (en) |
BR (1) | BR112021026316A2 (en) |
CA (1) | CA3144995A1 (en) |
FR (1) | FR3097556B1 (en) |
MX (1) | MX2022000210A (en) |
WO (1) | WO2020260799A1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR3095654B1 (en) * | 2019-05-03 | 2022-01-21 | Europeenne De Biomasse | Steam cracking control to improve the PCI of black pellets |
Family Cites Families (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101058948A (en) * | 2006-04-18 | 2007-10-24 | 中国科学院过程工程研究所 | Method of fractionating agronomic crop straw component and tissue |
CN105524947A (en) * | 2008-11-17 | 2016-04-27 | 希乐克公司 | biomass processing |
RU2518068C2 (en) * | 2008-12-15 | 2014-06-10 | ЗИЛХА БАЙОМАСС ФЬЮЭЛЗ АЙ ЭлЭлСи | Production of pellets or briquettes |
US8841495B2 (en) * | 2011-04-18 | 2014-09-23 | Gas Technology Institute | Bubbling bed catalytic hydropyrolysis process utilizing larger catalyst particles and smaller biomass particles featuring an anti-slugging reactor |
CN102949969B (en) * | 2011-08-26 | 2014-09-03 | 北京低碳清洁能源研究所 | Solid or high-viscosity carbonaceous material pyrolysis reactor system with downer mixer and catalytic heat carrier reheater and process thereof |
FR2982273B1 (en) * | 2011-11-09 | 2014-03-14 | Commissariat Energie Atomique | DRYING AND TORREFACTION REACTOR OF BIOMASS, PREFERABLY LIGNO-CELLULOSIC |
US8961628B2 (en) * | 2012-06-22 | 2015-02-24 | Sundrop Fuels, Inc. | Pretreatment of biomass using steam explosion methods |
CN104519991A (en) * | 2012-06-22 | 2015-04-15 | 三照普燃料公司 | Pretreating biomass using steam explosion before gasification |
ITTO20130888A1 (en) * | 2013-10-31 | 2015-05-01 | Biochemtex Spa | PROCEDURE FOR GROWING A MICROBIAL ORGANISM |
CN104212531A (en) * | 2014-09-25 | 2014-12-17 | 江南大学 | Method for preparing solid fuel by exploding biomass waste through external gas assisted by steam |
ES2975020T3 (en) * | 2015-05-13 | 2024-07-02 | Poet Res Incorporated | Procedures to reduce the size of lignocellulosic material, and related systems |
FI126555B (en) * | 2015-11-26 | 2017-02-15 | Valmet Technologies Oy | Biomass-based fuel arranged to reduce the chemical and / or mechanical influence of the flue gas on heat transfer surfaces and the method for its production |
CN206810626U (en) * | 2017-04-07 | 2017-12-29 | 贵州东峰锑业股份有限公司 | The Granulation Equipments of work is recycled in a kind of middle-low grade antimony ore production |
DE102017119573A1 (en) * | 2017-08-25 | 2019-02-28 | Viride Holding B.V. | Lignocellulosic biomass pellets for the production of organic molecules |
-
2019
- 2019-06-24 FR FR1906796A patent/FR3097556B1/en active Active
-
2020
- 2020-06-17 CN CN202080058605.XA patent/CN114555761A/en active Pending
- 2020-06-17 WO PCT/FR2020/051045 patent/WO2020260799A1/en unknown
- 2020-06-17 MX MX2022000210A patent/MX2022000210A/en unknown
- 2020-06-17 AU AU2020307195A patent/AU2020307195A1/en active Pending
- 2020-06-17 EP EP20742356.7A patent/EP3986990A1/en active Pending
- 2020-06-17 JP JP2021576621A patent/JP2022538234A/en active Pending
- 2020-06-17 KR KR1020227002224A patent/KR20220024849A/en unknown
- 2020-06-17 US US17/597,055 patent/US20220315851A1/en active Pending
- 2020-06-17 BR BR112021026316A patent/BR112021026316A2/en unknown
- 2020-06-17 CA CA3144995A patent/CA3144995A1/en active Pending
Also Published As
Publication number | Publication date |
---|---|
CA3144995A1 (en) | 2020-12-30 |
BR112021026316A2 (en) | 2022-06-07 |
EP3986990A1 (en) | 2022-04-27 |
US20220315851A1 (en) | 2022-10-06 |
WO2020260799A1 (en) | 2020-12-30 |
CN114555761A (en) | 2022-05-27 |
KR20220024849A (en) | 2022-03-03 |
FR3097556A1 (en) | 2020-12-25 |
FR3097556B1 (en) | 2021-11-26 |
MX2022000210A (en) | 2022-04-12 |
JP2022538234A (en) | 2022-09-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Suriapparao et al. | A review on role of process parameters on pyrolysis of biomass and plastics: present scope and future opportunities in conventional and microwave-assisted pyrolysis technologies | |
Ge et al. | Progress in microwave pyrolysis conversion of agricultural waste to value-added biofuels: a batch to continuous approach | |
Yao et al. | Characteristics of co-hydrothermal carbonization on polyvinyl chloride wastes with bamboo | |
Özsin et al. | TGA/MS/FT-IR study for kinetic evaluation and evolved gas analysis of a biomass/PVC co-pyrolysis process | |
CN110225958A (en) | Method and apparatus for producing bio-fuel | |
Yin | Microwave-assisted pyrolysis of biomass for liquid biofuels production | |
Vani et al. | Energy requirement for alkali assisted microwave and high pressure reactor pretreatments of cotton plant residue and its hydrolysis for fermentable sugar production for biofuel application | |
Ibrahim | Introductory chapter: pyrolysis | |
Shen | Dechlorination of poly (vinyl chloride) wastes via hydrothermal carbonization with lignin for clean solid fuel production | |
US9909078B2 (en) | Microwave produced pyrolysis oil from beneficiated organic-carbon-containing feedstock | |
Tripathi et al. | Effect of microwave frequency on dielectric properties of oil palm shell (OPS) and OPS char synthesized by microwave pyrolysis of OPS | |
JP2016010404A (en) | Method of processing biomass | |
Cheng et al. | Investigation of rapid conversion of switchgrass in subcritical water | |
CN113150813A (en) | Upgrading residues, heavy oils and plastics | |
Bai et al. | Investigation of improving the yields and qualities of pyrolysis products with combination rod-milled and torrefaction pretreatment | |
Manara et al. | Mediterranean agri-food processing wastes pyrolysis after pre-treatment and recovery of precursor materials: A TGA-based kinetic modeling study | |
Alimny et al. | Kinetics of reducing sugar formation from coconut husk by subcritical water hydrolysis | |
Lokmit et al. | A comparison of char fuel properties derived from dry and wet torrefaction of oil palm leaf and its techno-economic feasibility | |
Singh et al. | Recent advancement in microwave-assisted pyrolysis for biooil production | |
AU2020307195A1 (en) | Steam cracking process comprising a separation step and differential treatment of the obtained particles according to a threshold value | |
WO2023069159A1 (en) | Microwave heating applied to biomass and related features | |
Fang et al. | Ultrasonic pretreatment effect on the co-pyrolysis characteristics and products of bagasse and municipal sludge | |
US10287506B2 (en) | Biomass liquefaction process, and fuel oils and chemical materials prepared by the same | |
CN115698227A (en) | Method for producing combustible particles by improved steam cracking using heterogeneous biomass | |
AU2014308813B2 (en) | Biochar by microwave with beneficiated feedstock |